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Leiden University. The university to discover.
Abiotic Depletion Potential
- its philosophy from 1995 / 2002 –
Jeroen Guinée
Metals Industry Workshop on “Mineral resources in LCIA”
Natural History Museum, London, 14 October 2015
Leiden University. The university to discover.
Contents
• The ADP 1995/2002
– philosophy, definitions & choices made
– based on Guinée & Heijungs 1995 and van Oers et al.
2002
• Recent developments
• Conclusions
Contents
Leiden University. The university to discover.
Sources
Contents
http://www.leidenuniv.nl/cml/ssp/projects/lca2/report_abiotic_depletion_web.pdf
Leiden University. The university to discover.
Core issue addressed by ADP
• How serious is the depletion of one particular
natural resource in relation to that of another,
and how can this be expressed in terms of
characterization factors for these resources?
– A typical LCA question: how does an aluminum
beverage can compare to a PET or glass bottle with
respect to depletion of resources?
The ADP 1995/2002
Leiden University. The university to discover.
No scientifically „correct‟ method
• Abiotic depletion is a problem crossing the
economy-environment system boundary
– reserve depends on (future) technology
– is it an economic or environmental problem, or both?
• Depletion problem can‟t be verified empirically:
– „correct‟ definition of the problem
– total amount of resource
– result of depletion equation
can all not be validated empirically
The ADP 1995/2002
Leiden University. The university to discover.
Decisions/choices to take/make when
developing a method for depletion
• Abiotic and biotic
• Definition of the problem
• Stocks (deposits), funds and flows
• Renewable and non-renewable
• Concepts for assessing depletion
• Definition of availability
• Type of reserves
• Equation(s) for characterization factors (CFs)
The ADP 1995/2002
Leiden University. The university to discover.
Abiotic and biotic
• ADP: assess depletion of biotic resources
separately from abiotic resources
– because of the intrinsic value of biotic resources, their
source function and their role in the maintenance of
the life support system
– the weighting step of impact assessment provides an
opportunity to assign a different significance to biotic
depletion
• Focus in this presentation on abiotic resources
The ADP 1995/2002
Leiden University. The university to discover.
Definition of the problem
• Many possible definitions exist:
A. decrease of resource itself
B. decreasing world reserves of useful energy/exergy
C. contribution of current extraction processes to other
impact categories (no separate impact category)
D. incremental change in environmental impact of
extraction processes at some point in future (e.g.
result of having to extract lower-grade ores or
recover materials from scrap)
E. no environmental but economic problem
F. Etc.
The ADP 1995/2002
Leiden University. The university to discover.
Definition of problem
• ADP: „decreasing availability of natural resources
(in geosphere and/or anthroposphere)‟
– „abiotic resources‟: natural resources (including fossil
energy resources and minerals) which are regarded as
non-living
– resource depletion is an environmental problem in its
own right, while recognizing that views differ on this
– problem definition highly subjective -> no „perfect‟
method, no scientific consensus ….
The ADP 1995/2002
Leiden University. The university to discover.
Looking back … ADP only
addresses „depletion‟
• Depletion of a resource means that its amount
present on earth is being reduced. It refers to
geological/natural stocks
• Scarcity of a resource means that the amount
available for use is, or will soon be, insufficient
(“demand higher than supply flow”)
• Criticality of a resource means that it is scarce
and at the same time essential for the present
society
Source: Van der Voet (2013)
Leiden University. The university to discover.
Definition of problem
• ADP: „decreasing availability of natural
resources‟
– „abiotic resources‟: natural resources (including
fossil energy resources and minerals) which are
regarded as non-living
The ADP 1995/2002
„Depletion‟ only!
Leiden University. The university to discover.
Stocks, funds and flows
• Stocks/deposits: resources not regenerated
within human lifetimes: fossil fuels, minerals, etc.
• Funds: resources regenerated within human
lifetimes: groundwater and soil
• Flows: resources constantly regenerated: wind,
river water & solar energy (competitive use)
• ADP: focus on stocks
The ADP 1995/2002
Leiden University. The university to discover.
Renewable, non-renewable
• Commonly made distinction
• ADP: renewability (or regeneration) is parameter
in modeling of CFs rather than a criterion for
categorizing resource types
– comparable with the distinction between degradable
and non-degradable toxic substances.
The ADP 1995/2002
Leiden University. The university to discover.
Concepts for assessing depletion
• What determines the „decreasing availability” of
a given resource?
• Concepts for quantifying availability:
– the amount available (the reserve)
– annual de-accumulation: annual production (e.g. in
kg/yr) minus annual regeneration (same unit)
The ADP 1995/2002
We also touched upon aspects of
scarcity/criticality (e.g., substitution)
but didn‟t include these in the ADP;
still „depletion‟ only!
Leiden University. The university to discover.
Concepts: depletion measured by
economic data (e.g., price)
• Although the price of a resource can be
considered as a measure of its scarcity and
societal value, it reflects more than just that:
– structure of particular economic markets
– national social conditions reflected in labour cost
– power of mining companies with a monopoly
– identification of new reserves is very expensive
– etc.
The ADP 1995/2002
Leiden University. The university to discover. The ADP 1995/2002
Leiden University. The university to discover.
Concepts: physical data
• Physical data on reserves (“resources”) & de-
accumulation
• ADP: physical data on reserves & de-
accumulation; substitution not (yet) possible
The ADP 1995/2002
Leiden University. The university to discover.
Definition of availability
• „Narrow sense‟: availability in primary extraction
medium
– depletion: annual production exceeds annual regeneration
• „Broad sense‟: availability in geo- and anthroposphere
– elemental materials can never be depleted unless ..
competitive use rather than depletion
– increasing energy & solid waste amounts in extracting ever
lower concentrations, or in recovering dispersed resources
• ADP: „narrow sense‟
– while recognizing „broad sense‟ is preferable (this afternoon)
The ADP 1995/2002
„Urban‟/anthropogenic stocks
Leiden University. The university to discover.
Type of reserves
• Reserve base: reasonable potential for becoming economically and technically available
• Economic reserve: part of reserve base which could be economically extracted at time t
• Ultimate reserve: natural resources in earth crust
• Ultimately extractable reserves: reserves that can ultimately be technically extracted
The ADP 1995/2002
Mineral resource
Mineral reserve
Crustal content
Extractable global resource
Resource …confusion
Leiden University. The university to discover.
Earth crust volume (m3; average crust thickness of
17000 m and crust surface of 5.14x1014
m2)
Co
nce
ntr
atio
n (
kg/m
3)
Ultimately extractable reserve
Ultimate reserve
Reserve base
Economic reserveNo longer reported by USGS
Ultimately extractable reserves
best but unknown by definition
Economic and base reserves involve
economic considerations not directly
related to resource depletion
ADP: „ultimate reserves‟ second best yardstick,
but sensitivity analyses recommended with
other reserves!!
Extractable global resource
Mineral resource
Crustal content
Mineral reserve
The ADP 1995/2002
Leiden University. The university to discover.
Equation: R and/or DR rate
• A and B differ only in scale of their Rs – depletion of B more serious problem than A
• C and D differ only in scale of their DRs – extraction of 1 kg C more problematical than 1 kg of D
• Conclusion: both R and DR important – Another argument derives from renewable resources: seriousness of
extracting renewable resource is determined partly by degree of net de-accumulation (production/extraction minus regeneration)
resource
A
B
C
D
Reserve (Gton)
1
0.0001
1
1
De-accumulation Rate (Gton/yr) 0.000001
0.000001
0.1
0.0001
The ADP 1995/2002
Leiden University. The university to discover.
Equations
ADPi Abiotic Depletion Potential of resource i (-)
mi quantity of resource i extracted (kg)
i
ii mADPdepletionabiotic
The ADP 1995/2002
Leiden University. The university to discover.
Equations
Ri ultimate reserve of resource I (kg);
DRi de-accumulation rate (extraction/production minus regeneration) of resource i (kg·yr-1)
Rref ultimate reserve of the reference resource, antimony (kg)
DRref de-accumulation rate of Rref (kg·yr–1)
The indicator result is expressed in kg of the reference (ref) resource, viz. antimony.
2
2
ref
ref
i
i
i
R
DR
R
DR
ADP Assumed 0 for
abiotic resources
The ADP 1995/2002
Leiden University. The university to discover.
ADP 1995/2002: summary of choices
• Abiotic and biotic: separate impact categories
• Problem: decreasing availability of natural
resources
• Stocks (deposits)
• Renewable/non-renewable in modeling of CFs
• Concept: physical data on reserves & de-
accumulation
• „Narrow sense‟ availability
• Ultimate reserves
• Equation:
2
2
ref
ref
i
i
i
R
DR
R
DR
ADP
The ADP 1995/2002
Leiden University. The university to discover.
Recent developments
• For latest ADPs:
http://cml.leiden.edu/software/data-cmlia.html
– correction of mistakes
– no data updates by CML after 2002; but update of
some DR and R data by Frischknecht et al. (2012)
– finally split up the ADP in two subcategories (fossil
fuels and minerals).
• Schneider et al. (2011) AADP and ESP
• Gemechu et al. (2015) GeoPolRisk
Recent developments
Leiden University. The university to discover.
Substance cas no. group ADP kg antimony eq. / kg extraction 1,2,3
ultimate reserve4
reserve base reserve
aluminium (Al) 7429-90-5 element 1.09E-09 2.53E-05 2.14E-05 antimony (Sb) 7440-36-0 element 1.00E+00 1.00E+00 1.00E+00 arsenic (As) 7440-38-2 element 3.93E-03 2.40E+00 2.33E+00 barium (Ba) 7440-39-3 element 6.04E-06 3.37E-03 1.55E-02 beryllium (Be) 7440-41-7 element 1.26E-05 3.95E+00 bismuth (Bi) 7440-69-9 element 4.11E-02 4.49E+00 1.08E+01 boron (B) 7440-42-8 element 4.27E-03 5.28E-03 1.74E-02 bromine (Br) 7726-95-6 element 4.39E-03 cadmium (Cd) 7440-43-9 element 1.57E-01 1.11E+00 1.92E+00 chlorine (Cl) 7782-50-5 element 2.71E-05 chromium (Cr) 7440-47-3 element 4.43E-04 1.96E-05 3.77E-05 cobalt (Co) 7440-48-4 element 1.57E-05 2.56E-02 4.89E-02 copper (Cu) 7440-50-8 element 1.37E-03 2.50E-03 3.94E-03 gallium (Ga) 7440-55-3 element 1.46E-07 germanium (Ge) 7440-56-4 element 6.52E-07 1.95E+04 1.04E+04 gold (Au) 7440-57-5 element 5.20E+01 3.60E+01 3.99E+01 indium (In) 7440-74-6 element 6.89E-03 5.55E+02 1.15E+03 iodine (I2) 7553-56-2 element 2.50E-02 2.22E-03 3.10E-03 iron (Fe) 7439-89-6 element 5.24E-08 1.66E-06 3.64E-06 kalium (K;potassium)
7440-09-7 element 1.60E-08 9.00E-06 1.59E-05
lead (Pb) 7439-92-1 element 6.34E-03 1.50E-02 2.67E-02 lithium (Li) 7439-93-2 element 1.15E-05 1.33E-02 4.38E-02 magnesium (Mg) 7439-95-4 element 2.02E-09 manganese (Mn) 7439-96-5 element 2.54E-06 2.35E-05 5.80E-04
Result: updated CFs for different reserves
Source:
http://www.leidenuniv.nl/cml/ssp/projects/lca2/report_abiotic_depletion_web.pdf base year DR (extraction/de-accumulation) data: 1999 (USGS)
Recent developments
etc.
The reserve adopted may change the
decision-support provided Mineral reserve Mineral resource Crustal content
Leiden University. The university to discover.
Reserve adopted may change results
product A Product B
aluminium (Al) 5 0
antimony (Sb) 0,1 0,2
arsenic (As) 0 0,5
barium (Ba) 0 3
beryllium (Be) 0,5 0
iron (Fe) 0 5
Inventory result
Crustal content Mineral resource Mineral reserve
Leiden University. The university to discover.
Conclusions
• Impossible to define one correct method, since
correctness cannot be verified empirically
• Definition of the problem and all other choices
matter!!!
– other choices, and thus other methods, equally defensible
– “there‟s no such thing as the scientifically best method”
• Data ultimately extractable reserve will by definition
never be available
• CFs should be regularly updated, but are not!
– needs other „resources‟
Conclusions
Leiden University. The university to discover.
(Non-scientific) consensus?
Conclusions
Most choices cannot be validated
by experimental data
Updated!!
Mining & metals
industry
Other
stakeholders
Abiotic and biotic
Problem: decreasing availability of natural
resources („depletion‟)
Stocks (not funds and flows)
Renewable/non-renewable in modelling CFs ? ?
Physical data on reserves & de-accumulation /
Narrow sense availability (not yet broad) / ?
Ultimate reserves (crustal content) ?
Equation for characterization factors ? ?
Undeservedly neglected so far
Increasing reserves (base and
economic), but decreasing crustal
content and extractable global resource
Independent of chosen stock?
Data update or „regeneration‟?
= “Opportunity Cost world
view”?
„Depletion‟ versus „accessibility,
presence or readiness of a resource for
human use‟
„Depletion‟ (environmental aspect; LCA)
only versus „accessibility, presence
readiness‟ (socio-economic aspects;
scarcity/criticality; weighting or LCSA) = “Fixed Stock world view”?
Depending on problem definition,
world view (narrow/broad sense)
etc.; all choices are mutually
dependent!
Leiden University. The university to discover.
Why R2?
1. Share in reserves should also be assessed:
• Suppose a choice between applying 1 kg of resource A or 1 kg of
resource B, with following R and DR data:
– resource A: R=109 kg (and P=5×107 kg/yr)
– resource B: R=100 kg (and P=5 kg/yr).
– conclusion: A preferred, as R of A is affected far less by 1 kg extraction
• Now, suppose we adopt an equation R/DR (also known as R/P)
– R/DR of A and B is both 20 years
– resource A and B equally attractive in terms of depletion
2. Choice of units for ADP should not influence the final result for
abiotic depletion score
• Solution: Rz with z = y+1 and y>0 as reserve should be included
– R/DR method doesn‟t meet this requirement; see Guinée & Heijungs,
Environmental Toxicology & Chemistry (1995),14, 5, 917-925